This document discusses using electrochemical treatment to study the effect of process parameters on treating wastewater. It aims to optimize the removal of pollutants like phenol, dyes, and bacteria from textile industry effluent. The researchers will analyze how factors like pH, conductivity, electrolysis concentration, current density affect treatment. The electrochemical method uses electrodes to generate metal ions that neutralize pollutant charges and facilitate removal. The document examines this process in detail, outlines the experimental setup and method, and presents results showing increased phenol removal at higher pH levels and longer treatment times.

1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 2080
Study the Effect of Process Parameters during Electrochemical
Treatment of Wastewater
Sachin N. Golani1, Savan R. Ghelani2, Shivamsinh V. Jadav3, Kishan M. Kaneria4,
Prof. Baddi Prasad5 and Prof. Vishal Kumar Sandhwar6
1,2,3,4B.Tech. Chemical Engineering, Parul University
5,6Asst. Prof., Department of Chemical Engineering, Parul University, Vadodara, Gujarat, India
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Abstract - Disposal of industrial effluent wastewater
containinghazardouscomponentslikephenoland/orphenolic
compounds, unreacteddyes, ironsulphide, bacteria, lacticacid,
dissolved salt and other toxic compounds. We have to remove
these pollutants to reuse wastewater for industrial purpose.
There are so many methods to treat the effluent from
industries, but here we use most efficient method
electrochemical treatment. In present study, we will take the
sample of effluent from textile industries and also select the
electrodes that have remarkable binding characteristics to
remove pollutants, so special interest was devoted for
optimizing its uptake and studying its selectivity properties
under static and dynamic conditions. Also, we will study the
process parameters such as, effect of pH, conductivity,
electrolysis concentration, current density, etc. By using
electrochemical method, the pollutantsofeffluent wastewater
are mostly removed.
Key Words: EC treatment, wastewater, pH, type of
electrode, distance between electrodes, current density,
treatment time
1. INTRODUCTION
Today, the industrial wastewater is a major problem in
nowadays. It may contain hazardous pollutants like phenol
and/or phenolic compounds, suspended solids, bacteria,
dyes, etc. Because of their poor biodegradability and high
toxicity, it must be treated before we dischargeorreuse.The
Environmental Protection agency (EPA) decided that, the
quantity of phenol in the effluent wastewater is must be less
than 1 mg/L.
There are so many methods to treat wastewater such as
biological treatment,activatedcarbonadsorption,extraction,
oxidation andelectrochemical methods.Thesemethodshave
problems such as high cost, low efficiency, generation of
toxic compounds. Biological and electrochemical methods
are eco friendly methods means no harmful to environment.
The electrochemical treatment consists of electro-
oxidation, electrocoagulation, electroflotation, etc.
Comparing to other methods, it requireslessspace.Ithasthe
advantage of removing the smallest colloidal particles; the
smallest charged particleshavea greaterprobabilityof being
coagulated because of the electric field that sets them in
motion. It has also the advantage of producing a relatively
low amount of sludge.
In the present work, the removal of phenol from aqueous
solution was investigated using aluminum electrodes.
Several parameters, namely initial pH, conductivity, current
density, phenol concentration, NaCl concentration and
electrolysis time, were investigated for their effects on the
removal efficiency.
2. EC TREATMENT
Electrocoagulationneutralizestheelectrostaticcharge
on colloidal particles and facilitates coagulation and then
separates it from the solution. This treatment also prompts
precipitation of some of the metal sand salts. It involves the
situ generation of coagulants by dissolving electrically either
aluminum or iron ions from aluminum or iron electrodes,
respectively. The metal ions generation takes place at the
anode; hydrogen gas released from the cathode. The
hydrogengaswouldalsohelptofloatflocculatedparticlesout
of the water. In this process Al(OH)3 and Fe(OH)2 were
formed.
Fig. 2 Electrocoagulation cell
The chemical reaction taking place at the anode are given
as follows
For aluminum anode:
Al Al3+ + 3e-
At alkaline conditions
Al3+ + 3OH- Al(OH)3

2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 2081
At acidic conditions
Al3+ + 3H2O Al(OH)3 + 3H-
For iron anode:
Fe Fe2+ + 2e−
At alkaline conditions
Fe2+ + 2OH- Fe(OH)2
At acidic conditions
4Fe2+ + O2 + 2H2O 4 Fe3+ + 4OH-
In addition, there is oxygen evolution reaction
2H2O O2 + 4H+ + 4e−
The reaction at the cathode is
2H2O + 2e− H2 + 2OH-
The Al3+ or Fe2+ ions are very efficient coagulants for
particulates flocculating. The hydrolyzedaluminumionscan
form large networks of Al–O–Al–OH that can chemically
adsorb pollutants such as F-. Aluminum is usually used for
water treatment and iron for wastewater treatment. The
advantages of electrocoagulation include high particulate
removal efficiency, compact treatmentfacility,relativelylow
cost and possibility of complete automation.
3. EXPERIMENTAL DETAILS
3.1 Experimental Set up
The batch experimental setup is schematically shown in
fig. 3.1. The EC unit with monopolar electrodes in parallel
connection consists of an EC cell, a DC power supply and
electrodes. The aluminum cathode and aluminum anode
separated by a space of 2 cm and dipped in the wastewater.
The wastewater contains 300 mg/L phenol in water. The
electrolyte, 1 g NaCl was added to the phenol solution. The
EC treatment of wastewater was carried out in the glass
reactor. The volume of the rector was 991.85 cm2 [9.5
cm(dia.)*14 cm (h)]. There were four electrodes connected
in a monopolar mode in the electrochemical reactor, each
one with dimensions of 9.5 cm×2.5 cm×0.3 cm. Total area
submerged into the solution of the electrode is 53.95 cm2.
Fig. 3.1 Electrochemical cell
3.2 Experimental method
At the beginning of a run, the wastewater was fed into
the reactor and the pH adjusted to a desired value. The
electrodes were placed into the reactor. The reaction starts,
when the DC power supply was switched on. Because of
adding salt, aluminum salts reaction causes a 50% increase
in treatment time and power requirements. Eliminating the
salt formation at the anode could reduce this effect. We
performed no. of experiments by adjusting parameters pH
and treatment time. The cell was cleaned after each
experiment. Also, the electrodes were rinsed in the diluted
HCl solution after the each experiment to clean them.
Samples (10ml volume) were collected at pH = 3.2, 7.0 and
9.1 at different time intervals 30 min, 60 min, 90 min and
120 min respectively.
We can find % removal of phenol by
% Removal of phenol = (Ci - Cf)*100/Ci
Where, Ci is the initial phenol concentration (mg/L) and Cf
is the final phenol concentration (mg/L).
4. RESULT AND DISSCUSSION
4.1 Effect of pH
0
20
40
60
80
100
3.2 7 9.1
%Removal
pHFig. 4.1 Effect of pH on phenol removal efficiency
It has been established that the pH is an important
operating factor influencing the performance of
electrochemical process, current efficiency as well as the
solubility of metal hydroxide. To know this effect, pH of the
phenol solution was adjusted by using 1N NaOH and 1N
H2SO4. During the experimental work phenol removal

3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 04 | Apr 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 2082
efficiency was determined at different pH 3.2. 7.0 and 9.1 .
The results are shown in fig. 4.1 in which the variation of
removal efficiency of phenol with the solution initial pH
could be clearly identified. As the pH increases, the phenol
removal efficiency is increase.
4.2 Effect of treatment time
The treatment time is also an important parameter for
electrochemical treatment. It depends on the electrode
material and type of electrolyte. Here, in this experiment, as
the time increase, the amount of Al3+ ions released from the
electrodes will also increase, means moreamt.ofphenol will
be remove.
0
20
40
60
80
100
30 60 90 120
pH = 3.2
pH = 7.0
pH = 9.1
%Removal
Time (min)Fig. 4.2 Effect of treatment time on phenol removal
efficiency
CONCLUSION
Electrocoagulation of wastewater using Al electrodes
seems very effective method as relevant by present study. At
constant inner electrode distance and concentration of
phenol, as we increase the pH the rate of removal efficiency
of phenol will also increase. At pH = 9.1, the rate of phenol
removal is 77.7 %, which means we get high removal
efficiency at high pH. As the time increase, the rate of
removal of phenol will also increase. Also, the removal
efficiency of phenol is differentatdifferenttypesof electrode
materials.
ACKNOWLEDGEMENT
We are thankful to Prof. Baddi Prasad (Asst. Prof. of
chemical engineering, Parul University) and Prof. Vishal
Kumar Sandhwar (Asst. Prof. of chemical engineering, Parul
University) for their valuable advice during preparation of
the paper.
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